Page 105 - Materials Chemistry, Second Edition
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5.2 The environmental assessment—LCA             101
            5.2.1.4 Interpretation
              Interpretation is the last phase of an LCA, which is made up of summary and discussion
            about inventory analysis and impact assessment. The weakness of a product or a craft process
            will be identified, and relevant suggestions will be offered (ISO, 2006b).


            5.2.2 Research progress
              The research related to the environmental management standards ISO 14040 and ISO 14044
            made by the International Standardization Organization (ISO) have the most impact on LCA,
            which reflects the research consensus of LCA all over the word. At present, the main research
            directions of LCA include inventory analysis methods and impact assessment methods. The
            theory of the inventory analysis method, which places emphasis on normalizing the data ac-
            quisition, is reaching maturity. The research of the impact assessment impact consists of an
            assessment index system, impact assessment characterization model, the normalization of the
            assessment results, and so on. It is reflected in a rising series of environmental damage types,
            building mathematical models of life loss, and measuring and determining the toxicity of the
            pollutants to human health and ecosystems (Hertwich et al., 1999). Up to now, the method-
            ology and reference system of the LCIA is still developing forward continuously. There is no
            uniform standard accepted generally. There are different kinds of methods proposed, inter-
            nationally, to evaluate the impact, such as eco-scarcity method (Hanssen, 1999), environmen-
            tal priority solution (EPS) method (Steen et al., 2019), eco-indicator method (Spriensma, 1999),
            and environmental design industrial product (EDIP) method (Wenzel et al., 2000). The char-
            acteristics and weight approaches used by the environmental impact assessment methods
            above are listed in Table 5.1 (Hanssen, 1999; Finnveden, 1997).


            TABLE 5.1  Summary of some LCIA methodologies that include weighting approaches.
                                                  Eco-
            Assessment method                     scarcity   EPS    Eco-indicator  EDIP  LIME
            Major version                         1991       1992   1995        1997     2003
                                                  1997       1997   1999        2003
                                                             2000
            The range of application              Switzerland  World  Europe or  Denmark  Japan
                                                                    Netherlands
            The weighting selection of the  Average                             √
            characterization factors  value
                                      Specific scope         √      √                    √
                                      Goal-distance  √                          √
                                      method
                                      Expert                        √
                                      decision
                                      Monetization           √                           √
                                      method
   100   101   102   103   104   105   106   107   108   109   110